Automatic Tree Detection from Three-Dimensional Images

Total Page:16

File Type:pdf, Size:1020Kb

Automatic Tree Detection from Three-Dimensional Images remote sensing Article Automatic Tree Detection from Three-Dimensional ◦ Images Reconstructed from 360 Spherical Camera Using YOLO v2 Kenta Itakura and Fumiki Hosoi * Graduate School, University of Tokyo, Tokyo 113-8657, Japan; [email protected] * Correspondence: [email protected]; Tel.: +81-03-5841-5477 Received: 24 January 2020; Accepted: 15 March 2020; Published: 19 March 2020 Abstract: It is important to grasp the number and location of trees, and measure tree structure attributes, such as tree trunk diameter and height. The accurate measurement of these parameters will lead to efficient forest resource utilization, maintenance of trees in urban cities, and feasible afforestation planning in the future. Recently, light detection and ranging (LiDAR) has been receiving considerable attention, compared with conventional manual measurement techniques. However, it is difficult to use LiDAR for widespread applications, mainly because of the costs. We propose a method for tree measurement using 360◦ spherical cameras, which takes omnidirectional images. For the structural measurement, the three-dimensional (3D) images were reconstructed using a photogrammetric approach called structure from motion. Moreover, an automatic tree detection method from the 3D images was presented. First, the trees included in the 360◦ spherical images were detected using YOLO v2. Then, these trees were detected with the tree information obtained from the 3D images reconstructed using structure from motion algorithm. As a result, the trunk diameter and height could be accurately estimated from the 3D images. The tree detection model had an F-measure value of 0.94. This method could automatically estimate some of the structural parameters of trees and contribute to more efficient tree measurement. Keywords: automatic detection; deep learning; machine learning; spherical camera; structure from motion; three-dimensional (3D); tree trunk diameter; tree height; YOLO; 360-degree camera 1. Introduction Obtaining tree metrics has various applications in fields such as commercial forestry, ecology and horticulture. Tree structure measurement is fundamental for resource appraisal and commercial forest management [1]. In urban spaces, the knowledge of tree structure is important for their maintenance and for understanding their effects on urban environments. Trees in urban spaces have a significant influence upon urban environments through solar shading, transpiration, windbreaking, air purification and soundproofing [2]. Another important reason for measuring tree structure, including height and tree trunk diameter, is the creation of tree registries and regular monitoring for public safety. Therefore, trees in forests and cities play important roles, and the tree structural measurement is essential for their effective utilization. The conventional method is manual, and the tree measurement should be conducted one by one, meaning that the measurement is very tedious and time consuming. Besides, the manual measurement cannot be done frequently due to the hardness of the experiment. Then, measurement using terrestrial light detection and ranging (LiDAR) has attracted considerable attention. LiDAR is a three-dimensional (3D) scanner that provides highly accurate and dense 3D point clouds. A terrestrial LiDAR, which is placed on the ground, has been used widely. Remote Sens. 2020, 12, 988; doi:10.3390/rs12060988 www.mdpi.com/journal/remotesensing Remote Sens. 2020, 12, 988 2 of 20 Previous studies on the LiDAR have estimated tree trunk diameter, tree height [3–5], leaf area density [6,7], tree volume [8], biomass and leaf inclination angle [9,10]. However, when we use a LiDAR that should be stationed at one point for the measurement, it can require multiple measurements to cover the study sites, depending on the scale and shape of the study site. Recently, a light weight and portable LiDAR has been used for tree measurement [11]. This LiDAR measurement can be conducted while moving, enabling large area-measurement in a short period. Moreover, the field of view of LiDAR is large when the measurement is carried out during movement, and the maximum distance for measurement is not short (e.g., 100 m). Those LiDAR instruments also can be utilized with unmanned aerial systems or drones [12–14]. By combining LiDAR with those platforms, the 3D data of large area including numerous trees can be easily obtained. However, the instrument is costly, and the measurement process, such as in forests, is laborious. Moreover, LiDAR itself cannot obtain the color value. Structure from Motion (SfM) is a photogrammetric approach for 3D imaging, where the camera positions and orientations are solved automatically after extracting image features to recover 3D information [15]. Liang et al. [16] showed that the mapping accuracy of a plot level and an individual-tree level was 88 %, and the root mean squared error of the diameter at breast height (DBH) estimates of individual trees was 2.39 cm, which is acceptable for practical applications. Additionally, the results achieved using terrestrial LiDAR are similar. Piermattei et al. [17] concluded that the SfM approach was an accurate solution to support forest inventory for estimating the number and the location of trees. In addition, the DBHs and stem curve up to 3 m above the ground. Qiu et al. [18] developed a terrestrial photogrammetric measurement system for recovering 3D information for tree trunk diameter estimation. As a result, the SfM approach with a consumer-based, hand-held camera is considered to be an effective method for 3D tree measurement. However, the field of view of cameras is limited, compared with LiDAR [19]. For example, to capture trees on the right and left side in the direction of movement, the measurement should be conducted at least twice for both sides. Moreover, a certain distance is necessary from the target to cover the whole tree. However, it is sometimes impossible to achieve this distance because of restrictions in the field. Recently, 360◦ spherical cameras that capture images in all directions have been used widely. The field of view of the 360◦ spherical camera is omnidirectional, while that of the mobile LiDAR is not (e.g., Velodyne VLP-16: vertical 15 ). In addition, color information can be obtained as well. Moreover, it ± ◦ is much lighter and inexpensive than LiDAR. As mentioned, the 360◦ spherical camera has advantages of both a LiDAR and a camera. These are omnidirectional view, availability of color information, light weight and affordable cost. Further, 3D point clouds can be reconstructed from the spherical images using SfM [20,21]. A previous study estimated the sky view factor with the 360◦ spherical camera with color information. This sky view factor is a ratio of the sky in the upper hemisphere, and it is an important index in many environmental studies [22]. However, structural measurement via 3D imaging has not been explored thus far. Further, if structural measurement can be performed using a spherical camera, automatic tree detection, which leads to automatic tree analysis, is required. Automatic tree detection of each tree enables the estimation of properties such as tree trunk diameter and tree height. Two approaches for automatic tree detection from the spherical images can be considered. The first is to detect trees from the reconstructed 3D images using a 3D image processing technique. For example, a tree identification method with a cylinder or a circle fitting the tree trunk is used popularly [23,24]. As another method [25,26], it utilizes the intensity of the reflectance of the laser beam from the LiDAR for tree detection. However, 3D image processing requires considerable memory size, and the calculation cost tends to be large. In addition, when reconstructing 3D images using SfM, there are many missing points, owing to the absence of matching points among the input images around the missing area, and the mis-localized points. This makes it difficult to detect trees from 3D images. Remote Sens. 2020, 12, 988 3 of 20 The second approach is to detect trees in two-dimensional (2D) images and reconstruct the 3D images with the information of each tree identification. As mentioned above, if the 3D images recovered from SfM are not complete because of missing points, the resolution and accuracy of the input 2D images will be much higher than the reconstructed 3D images. Therefore, it is assumed that the detection from 2D images is more accurate than from 3D images. One of the biggest challenges in the tree detection from 2D images is the presence of numerous objects in the background. 2D image processing cannot utilize depth information, unlike 3D image processing. Recently, the methodology for detecting the target automatically has been rapidly improved, because of the use of a deep learning-based technique. A region-convolutional neural network (R-CNN) [27] applied deep learning for target detection for the first time. The traditional features are replaced by features extracted from deep convolution networks [28]. Fast R-CNN and Faster R-CNN have been developed for overcoming the disadvantages of the long processing time of R-CNN [29,30]. Nowadays, other algorithms for object detection are available, such as YOLO and SSD [31,32]. These methods operate at a very fast speed with high accuracy. The YOLO model processes images at more than 45 frames per second. The speed is increasing because the algorithm is being updated. Hence, real-time based detection is now possible. We used the YOLO v2 model [33], and the tree detector constructed based on YOLO v2 is called YO v2 detector in this paper. In this study, the tree images were obtained with a 360◦ spherical camera, and its 3D reconstruction was done using SfM to estimate the tree trunk diameter and tree height. Next, the tree detector was developed based on the YOLO v2 network. The 3D point clouds were reconstructed with information from the tree detection. Finally, the trees in the 3D point clouds were automatically detected.
Recommended publications
  • Restoration of Dry Forests in Eastern Oregon
    Restoration of Dry Forests in Eastern Oregon A FIELD GUIDE Acknowledgements Many ideas incorporated into this field guide originated during conversations between the authors and Will Hatcher, of the Klamath Tribes, and Craig Bienz, Mark Stern and Chris Zanger of The Nature Conservancy. The Nature Conservancy secured support for developing and printing this field guide. Funding was provided by the Fire Learning Network*, the Oregon Watershed Enhancement Board, the U.S. Forest Service Region 6, The Nature Conservancy, the Weyerhaeuser Family Foundation, and the Northwest Area Foundation. Loren Kellogg assisted with the discussion of logging systems. Bob Van Pelt granted permission for reproduction of a portion of his age key for ponderosa pine. Valuable review comments were provided by W.C. Aney, Craig Bienz, Mike Billman, Darren Borgias, Faith Brown, Rick Brown, Susan Jane Brown, Pete Caligiuri, Daniel Donato, James A. Freund, Karen Gleason, Miles Hemstrom, Andrew J. Larson, Kelly Lawrence, Mike Lawrence, Tim Lillebo, Kerry Metlen, David C. Powell, Tom Spies, Mark Stern, Darin Stringer, Eric Watrud, and Chris Zanger. The layout and design of this guide were completed by Keala Hagmann and Debora Johnson. Any remaining errors and misjudgments are ours alone. *The Fire Learning Network is part of a cooperative agreement between The Nature Conservancy, USDA Forest Service and agencies of the Department of the Interior: this institution is an equal opportunity provider. Suggested Citation: Franklin, J.F., K.N. Johnson, D.J. Churchill, K. Hagmann, D. Johnson, and J. Johnston. 2013. Restoration of dry forests in eastern Oregon: a field guide. The Nature Conservancy, Portland, OR.
    [Show full text]
  • Tree Density and Forest Productivity in a Heterogeneous Alpine Environment: Insights from Airborne Laser Scanning and Imaging Spectroscopy
    Article Tree Density and Forest Productivity in a Heterogeneous Alpine Environment: Insights from Airborne Laser Scanning and Imaging Spectroscopy Parviz Fatehi 1,*, Alexander Damm 1, Reik Leiterer 1, Mahtab Pir Bavaghar 2, Michael E. Schaepman 1 and Mathias Kneubühler 1 1 Remote Sensing Laboratories (RSL), University of Zurich, Winterthurerstrasse 190, 8057 Zurich, Switzerland; [email protected] (A.D.); [email protected] (R.L.); [email protected] (M.E.S.); [email protected] (M.K.) 2 Center for Research and Development of Northern Zagros Forests, Faculty of Natural Resources, University of Kurdistan, 66177-15175 Sanandaj, Iran; [email protected] * Correspondence: [email protected]; Tel.: +41-44-635-6508 Academic Editors: Christian Ginzler and Lars T. Waser Received: 8 March 2017; Accepted: 9 June 2017; Published: 16 June 2017 Abstract: We outline an approach combining airborne laser scanning (ALS) and imaging spectroscopy (IS) to quantify and assess patterns of tree density (TD) and forest productivity (FP) in a protected heterogeneous alpine forest in the Swiss National Park (SNP). We use ALS data and a local maxima (LM) approach to predict TD, as well as IS data (Airborne Prism Experiment—APEX) and an empirical model to estimate FP. We investigate the dependency of TD and FP on site related factors, in particular on surface exposition and elevation. Based on reference data (i.e., 1598 trees measured in 35 field plots), we observed an underestimation of ALS-based TD estimates of 40%. Our results suggest a limited sensitivity of the ALS approach to small trees as well as a dependency of TD estimates on canopy heterogeneity, structure, and species composition.
    [Show full text]
  • Implications of Selective Harvesting of Natural Forests for Forest Product Recovery and Forest Carbon Emissions: Cases from Tarai Nepal and Queensland Australia
    Article Implications of Selective Harvesting of Natural Forests for Forest Product Recovery and Forest Carbon Emissions: Cases from Tarai Nepal and Queensland Australia Bishnu Hari Poudyal, Tek Narayan Maraseni * and Geoff Cockfield Centre for Sustainable Agricultural Systems, University of Southern Queensland, Queensland 4350, Australia * Correspondence: [email protected] Received: 5 July 2019; Accepted: 13 August 2019; Published: 15 August 2019 Abstract: Selective logging is one of the main natural forest harvesting approaches worldwide and contributes nearly 15% of global timber needs. However, there are increasing concerns that ongoing selective logging practices have led to decreased forest product supply, increased forest degradation, and contributed to forest based carbon emissions. Taking cases of natural forest harvesting practices from the Tarai region of Nepal and Queensland Australia, this study assesses forest product recovery and associated carbon emissions along the timber production chain. Field measurements and product flow analysis of 127 commercially harvested trees up to the exit gate of sawmills and interaction with sawmill owners and forest managers reveal that: (1) Queensland selective logging has less volume recovery (52.8%) compared to Nepal (94.5%) leaving significant utilizable volume in the forest, (2) Stump volume represents 5.5% of total timber volume in Nepal and 3.9% in Queensland with an average stump height of 43.3 cm and 40.1 cm in Nepal and Queensland respectively, (3) Average sawn timber output from the harvested logs is 36.3% in Queensland against 3 3 61% in Nepal, (4) Nepal and Queensland leave 0.186 Mg C m− and 0.718 Mg C m− on the forest floor respectively, (5) Each harvested tree damages an average of five plant species in Nepal and four in Queensland predominantly seedlings in both sites, and (6) Overall logging related total emissions in 3 3 Queensland are more than double (1.099 Mg C m− ) those in Nepal (0.488 Mg C m− ).
    [Show full text]
  • How Should We Measure the DBH of Multi-Stemmed Urban Trees? T Yasha A.S
    Urban Forestry & Urban Greening 47 (2020) 126481 Contents lists available at ScienceDirect Urban Forestry & Urban Greening journal homepage: www.elsevier.com/locate/ufug How should we measure the DBH of multi-stemmed urban trees? T Yasha A.S. Magarika,*, Lara A. Romanb, Jason G. Henningc a Yale School of Forestry & Environmental Studies, 195 Prospect Street, New Haven, CT, 06511, USA b USDA Forest Service, Philadelphia Field Station, 100 N. 20thSt., Suite 205, Philadelphia, PA, 19103, USA c The Davey Institute and USDA Forest Service, 100 N. 20thSt., Suite 205, Philadelphia, PA, 19103, USA ARTICLE INFO ABSTRACT Handling Editor: Justin Morgenroth Foresters use diameter at breast height (DBH) to estimate timber volumes, quantify ecosystem services, and ffi Keywords: predict other biometrics that would be di cult to directly measure. But DBH has numerous problems, including Diameter at breast height a range of “breast heights” and challenges with applying this standard to divergent tree forms. Our study focuses Crown diameter on street trees that fork between 30 and 137 cm of height (hereafter “multi-stemmed trees”), which researchers Ecological monitoring have identified as particularly challenging in the ongoing development of urban allometric models, as well as Street tree consistency in measurements across space and time. Using a mixed methods approach, we surveyed 25 urban Tree allometry forestry practitioners in twelve cities in the northeastern United States (US) about the measurement and man- Urban forest agement of multi-stemmed street trees, and intensively measured 569 trees of three frequently planted and commonly multi-stemmed genera (Malus, Prunus, and Zelkova) in Philadelphia, PA, US.
    [Show full text]
  • A Treemendous Educator Guide
    A TREEmendous Educator Guide Throughout 2011, we invite you to join us in shining a deserving spotlight on some of Earth’s most important, iconic, and heroic organisms: trees. To strengthen efforts to conserve and sustainably manage trees and forests worldwide, the United Nations has declared 2011 as the International Year of Forests. Their declaration provides an excellent platform to increase awareness of the connections between healthy forests, ecosystems, people, and economies and provides us all with an opportunity to become more aware, more inspired, and more committed to act. Today, more than 8,000 tree species—about 10 percent of the world’s total—are threatened with extinction, mostly driven by habitat destruction or overharvesting. Global climate change will certainly cause this number to increase significantly in the years to come. Here at the Garden, we care for many individual at-risk trees (representing 48 species) within our diverse, global collection. Many of these species come from areas of the world where the Garden is working to restore forest ecosystems and the trees in them. Overall, we have nearly 6,000 individual trees in our main Garden, some dating from the time of founder Henry Shaw. Thousands more trees thrive at nearby Shaw Nature Reserve, as part of the Garden’s commitment to native habitat preservation, conservation, and restoration. Regardless of where endangered trees are found—close to home or around the world—their survival requires action by all of us. The Great St. Louis Tree Hunt of 2011 is one such action, encouraging as many people as possible to get out and get connected with the spectacular trees of our region.
    [Show full text]
  • As the Piedmont Regional Forester and Also the Incident Commander
    April 2018 As the Piedmont Regional Forester and also the Incident Commander (IC) of our Incident Management Team (IMT), I’d like to share some of what I have learned in my nearly 35 years with the Commission about how leadership opportunities can make each one of us the best March Fire Photos version of ourselves. Page 8 These thoughts reinforce several of our Our IMT is founded on the three new State Forester’s five overarching Wildland Fire Leadership Principles of goals, including providing a safe, Duty, Respect, and Integrity. Let’s look desirable and friendly workplace that at them and how each one can help us relies on good communications, which to be the best version of ourselves while results in outstanding customer service. striving for our goals. I believe that to be successful you must Duty – Be proficient in your job daily, set goals and then focus on the progress both technically and as a leader you make towards those goals. But one - Make sound and timely decisions must be able to measure that progress; Tree Farm Legislative Day - Ensure tasks are understood, Page 16 if you can’t measure it, you can’t change it. So as we make progress we should supervised, and accomplished celebrate those accomplishments. - Develop your subordinates for the This celebration of progress in the end future helps us to persevere towards those Respect - Know your subordinates and goals. Because as we sense that we are look out for their well-being making progress, we tend to be filled - Build the team with passion, energy, enthusiasm, purpose and gratitude.
    [Show full text]
  • Field Guideline for Biomass Baseline Survey
    GHG Emission Assessment Guideline Volume II: Aboveground Biomass Field Guide for Baseline Survey FEDERAL DEMOCRATIC REPUBLIC OF ETHIOPIA MINISTRY OF AGRICULTURE ADDIS ABABA ETHIOPIA About the authors: Dr. Tadesse Woldemariam Acknowledgements The authors would like to thank the Ministry of Agriculture – Natural Resources Management Directorate – CRGE unit for providing financial assistance and technical support in the development of this guideline. Produced by Echnoserve Consulting April 2015 Front cover photo: Echnoserve Credit: Bayu Nebsu & Assefa Tadesse i | P a g e Table of Contents List of Tables List of Figures List of Acronyms IV CHAPTER ONE 1 1. Introduction 1 1.1. Background 1 1.2 Objectives of the Guideline 3 1.3. Methodology 3 CHAPTER TWO 4 2. Concepts and Definitions terms 4 2.1 The concept of Climate change 4 2.2. Greenhouse Gases in AFOLU 5 2.2.1. Emission and Removal Processes 6 2.3. Definition of some key terms 6 2.3.1 Carbon pool definitions and non-CO2 gases 8 2.3.2 Flux of Carbon Pools 10 2.4 Why Carbon Inventory 11 2.4.1 Carbon Pools and Measurement Frequency for Carbon Inventory 12 2.5 Carbon Inventory for Climate Change Mitigation Projects or Programmes 13 CHAPTER THREE 14 3. Methodological Issues in Land-Based Carbon Inventory Projects 14 3.1 Baseline 14 3.1.1 Fundamental Steps in Establishing a Baseline 15 3.2 Generic Methods for Inventory of Carbon Pools 16 3.2.2 Carbon “Gain–Loss” Method 17 3.2.3 Carbon “Stock-Difference” Method 17 3.2.4 Comparison of “Gain–Loss” and “Stock-Difference” Approaches 18 3.3 Methodological Options for Estimating Carbon Pools 18 CHAPTER FOUR 20 4.
    [Show full text]
  • Conducting a Simple Timber Inventory Conducting a Simple Timber Inventory Jason G
    PB1780 Conducting a Simple Timber Inventory Conducting a Simple Timber Inventory Jason G. Henning, Assistant Professor, and David C. Mercker, Extension Specialist Department of Forestry, Wildlife and Fisheries Purpose and Audience This publication is an introduction to the terminology The authors are confident that if the guidelines and methodology of timber inventory. The publication described herein are closely adhered to, someone with should allow non-professionals to communicate minimal experience and knowledge can perform an effectively with forestry professionals regarding accurate timber inventory. No guarantees are given timber inventories. The reader is not expected to that methods will be appropriate or accurate under have any prior knowledge of the techniques or tools all circumstances. The authors and the University of necessary for measuring forests. Tennessee assume no liability regarding the use of the information contained within this publication or The publication is in two sections. The first part regarding decisions made or actions taken as a result provides background information, definitions and a of applying this material. general introduction to timber inventory. The second part contains step-by-step instructions for carrying out Part I – Introduction to Timber a timber inventory. Inventory A note of caution The methods and descriptions in this publication are What is timber inventory? not intended as a substitute for the work and advice Why is it done? of a professional forester. Professional foresters can tailor an inventory to your specific needs. Timber inventories are the main tool used to They can help you understand how an inventory determine the volume and value of standing trees on a may be inaccurate and provide margins of error for forested tract.
    [Show full text]
  • School of Renewable Natural Resources Newsletter, Fall 2009 Louisiana State University and Agricultural & Mechanical College
    Louisiana State University LSU Digital Commons Research Matters & RNR Newsletters School of Renewable Natural Resources 2009 School of Renewable Natural Resources Newsletter, Fall 2009 Louisiana State University and Agricultural & Mechanical College Follow this and additional works at: http://digitalcommons.lsu.edu/research_matters Recommended Citation Louisiana State University and Agricultural & Mechanical College, "School of Renewable Natural Resources Newsletter, Fall 2009" (2009). Research Matters & RNR Newsletters. 13. http://digitalcommons.lsu.edu/research_matters/13 This Book is brought to you for free and open access by the School of Renewable Natural Resources at LSU Digital Commons. It has been accepted for inclusion in Research Matters & RNR Newsletters by an authorized administrator of LSU Digital Commons. For more information, please contact [email protected]. Fall 2009 Managing resources and protecting the environment . making a difference in the 21st century Outdoor Classrooms School of Renewable Natural Resources 1 ers and alumni in the near future. Once it is completed Director’s Comments we will post our entire strategic plan on our Web page (www.rnr.lsu.edu), which will include our mission and Another academic year has passed vision statements, identified programs of excellence, and the School continues to make goals we will strive to achieve and specific objectives improvements in our core mission on how to achieve these goals. This will be an ongo- areas of teaching, research and exten- ing process and we encourage each of you to provide sion. Our undergraduate and gradu- suggestions on how we can continue to improve the ate enrollment has shown increases, mission of the School. we continue to be leaders in the Recent restructuring of our graduate programs was AgCenter in publication numbers and extra-mural grant undertaken to allow more integration across historic funds, and our extension and service contacts continue degree boundaries, which should result in students to increase.
    [Show full text]
  • Field Manual
    NATIONAL FOREST INVENTORY LEBANON Field Manual Compiled by A. Branthomme 2nd Edition: M. Saket, D. Altrell, P. Vuorinen, S. Dalsgaard & L.G.B Andersson Rome, 2004 FAO Forestry Department Ver 6.3 Revised 29.04.2004 by S. Dalsgaard National Forest Inventory - Field Manual Contents Introduction ................................................................................................................................................................. 4 1. Sampling design................................................................................................................................................... 4 1.1 Tract selection and distribution ..................................................................................................................... 4 1.2 Tract description............................................................................................................................................ 6 2. Land use/forest type classification ..................................................................................................................... 8 3. Field work: preparation and data collection .................................................................................................. 11 3.1 Fieldwork .................................................................................................................................................... 11 3.2 Field crew composition ..............................................................................................................................
    [Show full text]
  • Forestry CD Activity Guide Cover, You Will See a Forester Demonstrating the Correct Technique to Determine DBH with a Biltmore Stick
    chapter 8/27/56 9:33 AM Page 2 Source: Project Learning Tree K-8 Activity Guide: page 243 2 chapter 8/27/56 9:33 AM Page 3 TOOLS USED IN FORESTRY Biltmore stick – Clinometer – Diameter Tape – Increment Borer – Wedge Prism Throughout history, the need for measurement has been a necessity for each civilization. In commerce, trade, and other contacts between societies, the need for a common frame of reference became essential to bring harmony to interactions. The universal acceptance of given units of measurement resulted in a common ground, and avoided dissension and misunderstanding. In the early evolvement of standards, arbitrary and simplified references were used. In Biblical times, the no longer familiar cubit was an often-used measurement. It was defined as the distance from the elbow to a person’s middle finger. Inches were determined by the width of a person’s thumb. According to the World Book Encyclopedia, “The foot measurement began in ancient times based on the length of the human foot. By the Middle Ages, the foot as defined by different European countries ranged from 10 to 20 inches. In 1305, England set the foot equal to 12 inches, where 1 inch equaled the length of 3 grains of barley dry and round.”1 [King Edward I (Longshanks), son of Henry III, ruled from 1272–1307.] Weight continues to be determined in Britain by a unit of 14 pounds called a “stone.” The origin of this is, of course, an early stone selected as the arbitrary unit. The flaw in this system is apparent; the differences in items selected as standards would vary.
    [Show full text]
  • Guide to the Forest History Society Photograph Collection [PDF]
    __________________________________________________________________________ GUIDES TO FOREST AND CONSERVATION HISTORY OF NORTH AMERICA, No. 7 __________________________________________________________________________ GUIDE to the FOREST HISTORY SOCIETY PHOTOGRAPH COLLECTION __________________________________________________________________________ Forest History Society, Inc. 1989; Revised Ed. 2003, 2006, 2017 __________________________________________________________________________ i ____________________________________________________________________ Table of Contents ____________________________________________________________________ Table of Contents......................................................................................................................... ii Introduction................................................................................................................................ iii Notes Re Revised Edition ............................................................................................................. iv Index to the Forest History Society Photograph Collection ............................................................. 1 Photographs of Individuals .........................................................................................................17 Auxiliary Photograph Collections .................................................................................................23 ii ____________________________________________________________________ Introduction ____________________________________________________________________
    [Show full text]